1,830 results

Staying Healthy: Industry organisations’ influence on behaviours and services used by fishers

Project number: 2012-402
Project Status:
Completed
Budget expenditure: $98,308.00
Organisation: Deakin University Geelong Waterfront Campus
Project start/end date: 19 Jun 2012 - 4 May 2014
Contact:
FRDC

Need

Research has found that fishers are subject to a multitude of stressors, including those relating to government policies and co-management challenges, a fluctuating market place, crew cohesion and on-shore social relationships, and the pressures of working in a dangerous workplace. Compounding the well-known physical dangers associated with the fishing industry, these factors all place pressure on fisher mental wellbeing, which in turn contributes to issues such as clinically diagnosed anxiety disorders, poor eating habits and substance abuse, eg, evidence from around the world suggests that the particular stresses of fishing contribute to higher than average rates of smoking among fishers.
Findings from the RIRDC-funded project Staying Healthy: Behaviours and services used by farmers and fishers indicate that while participants from certain farming industry areas have benefited from industry involvement in health and wellbeing, including in relation to mental health, fishers are less likely to report that industry associations have helped them access health and wellbeing information or programs. Some farmers described significant lifestyle changes after participating in programs that were promoted, sponsored or facilitated by trusted industry organisations. As well, recent research (Brooks, 2011, Health and Safety in the Australian Fishing Industry, RIRDC, Canberra) has found a lack of awareness of occupational health and safety among fishers. The Research Audit of Social Sciences Fisheries Research (Clarke, 2009) noted research findings that social wellbeing is related to financial wellbeing, and that social networking is negatively affected by working hours, suggesting a place for an industry specific approach to social connection and mental health. There appears to be a broking role for industry groups and organisations in enhancing the health of the fishing workforce. This project will identify strategies for industry and fishing community organisations to take on this role in effective, but cost and resource efficient, ways.

Objectives

1. to explore how industry supports fisher physical health and mental wellbeing
2. to develop and trial a set of case studies and best practice guidelines for industry organisations in enhancing fisher health and wellbeing in collaboration with industry, fishing communities and health stakeholders
3. to evaluate the case studies and best practice guidelines

Developing tagging models and validating assumptions for estimating key fishery assessment parameters in rock lobster fisheries

Project number: 2003-051
Project Status:
Completed
Budget expenditure: $409,509.00
Principal Investigator: Stewart Frusher
Organisation: University of Tasmania (UTAS)
Project start/end date: 19 Jul 2003 - 1 Jul 2007
Contact:
FRDC

Need

There is a common need in the assessment of all fisheries to obtain precise estimates of exploitation rates and/or biomass. In the Tasmanian rock lobster fishery, biomass is a key performance indicator and change in biomass is the primary driver for recommendations of future Total Allowable Commercial Catch (TACC) allocations by the Fisheries Advisory Committee. In recognition of this need, both the Tasmanian
Government (1992-1997) and FRDC (1997-2001) have funded projects to investigate methods to estimate biomass independent of the fishery.

Fishery independent estimates are essential because estimates derived from fisher’s catch and effort are often biased as exemplified by the change in the link between catch rate and abundance following the introduction of the ITQ management system in Tasmania (FRDC 1999/140). Although initially promising, exploitation rate and biomass estimates based on changes in the population during the fishing season proved unreliable (FRDC 1997/101). Both the Industry and Managers have identified the need to explore new methods to obtain precise estimates of these important performance indicators.

Multi-year tagging models have been identified as a promising way of estimating these parameters because they address the failings (variable catchability and recruitment) in the population derived estimators. Initial trials in northwestern Tasmania proved very successful and support the potential of this approach. However, tag returns from fishers are unpredictable and there is an immediate need to
determine ways of improving tag reporting rate to optimise the output of tag based models. Furthermore, the models applied to northwestern Tasmania relied on a minimum of two tagging events occurring each fishing season. As each tagging event occurred during a different period of the moult cycle, there is a need to validate the tag retention and tag induced mortality rates associated with these different tagging times. Other factors relating to size, sex, damage and their interactions with different tagging times also need further investigation. A careful evaluation of other means of improving the precision of estimates from tagging models is seen as necessary, prior to the implementation of a large scale tagging program.

Validating the assumptions associated with the use of tagging models, demonstrating ways to test for these assumptions and the precision of fishery assessment outputs is needed prior to recommending these models for use in other fisheries.

Objectives

1. To develop methods for maximising and better estimating tag reporting rate.
2. To evaluate different tagging methods in rock lobsters with respect to tag induced mortality, tag loss and the likelihood of recaptured tags being reported.
3. To determine the variability in tag loss, tag induced mortality and tag recapture rates associated with the time of tagging and demonstrate the impact that these have on mortality estimates.
4. To develop a fishery-based mark recapture model that estimates both fishing mortality and natural mortality and catchability, and demonstrates the precision of these parameters based on a number of data options.

Final report

ISBN: 978-1-86295-504-2
Author: Stewart Frusher
Final Report • 2017-09-29
2003-051-DLD.pdf

Summary

Tagging is an important tool for estimating key fisheries parameters such as fishing mortality, natural mortality and growth. This project identified the need for future tagging projects to undertake preliminary studies to determine the impact of tagging on both growth and survival, and we developed a new method for obtaining in situ measurements. While aquaria studies have demonstrated that the timing of tagging in relation to the lobster moult cycle can have an impact on tag-induced mortality, these studies estimated that the impacts were low. The in situ method in our study found similar moult cycle impacts but our impact estimates were substantially higher than previously considered.
 
New tagging projects for lobster should evaluate the use of PIT tags as this project demonstrated the ‘proof of concept’ in obtaining a 100% tag reporting rate by scanners placed at strategic locations on board fishing vessels. With as few as 10% of the fleet having scanners, PIT tagging proved to be cost beneficial compared to conventional T-bar tags. As PIT tags are normally imbedded in the muscle of an animal, they are ‘invisible’ to potential reporters (e.g. fishers). A hybrid T-bar tag developed and tested in this project combined a T-bar tag and a PIT tag so that the PIT tag remained visible to fishers for reporting on vessels that did not contain scanners. An additional benefit of the hybrid tag was that it removed the potential for the PIT tag to be ingested.
 
The development of an ‘exact time’ survival model that followed the fate of individual tags enables tagging programs to be more flexible in the release of tags. Previous multi-year tagging models required releases to be aggregated to a single release period during a specific tagging event (i.e. mean day of all releases for a tagging event). The new model allows for tagging projects to be more flexible in their design and incorporate tags released at any time. This would allow for inclusion of tagged animals released by fishers throughout the fishing season (e.g. berried female lobsters). The ‘exact time’ model also enabled finer scale (weeks, months etc) estimates of catchability to be estimated in addition to mortality rates, thus increasing the information obtained from a tagging study.
 
Final Report • 2017-09-29
2003-051-DLD.pdf

Summary

Tagging is an important tool for estimating key fisheries parameters such as fishing mortality, natural mortality and growth. This project identified the need for future tagging projects to undertake preliminary studies to determine the impact of tagging on both growth and survival, and we developed a new method for obtaining in situ measurements. While aquaria studies have demonstrated that the timing of tagging in relation to the lobster moult cycle can have an impact on tag-induced mortality, these studies estimated that the impacts were low. The in situ method in our study found similar moult cycle impacts but our impact estimates were substantially higher than previously considered.
 
New tagging projects for lobster should evaluate the use of PIT tags as this project demonstrated the ‘proof of concept’ in obtaining a 100% tag reporting rate by scanners placed at strategic locations on board fishing vessels. With as few as 10% of the fleet having scanners, PIT tagging proved to be cost beneficial compared to conventional T-bar tags. As PIT tags are normally imbedded in the muscle of an animal, they are ‘invisible’ to potential reporters (e.g. fishers). A hybrid T-bar tag developed and tested in this project combined a T-bar tag and a PIT tag so that the PIT tag remained visible to fishers for reporting on vessels that did not contain scanners. An additional benefit of the hybrid tag was that it removed the potential for the PIT tag to be ingested.
 
The development of an ‘exact time’ survival model that followed the fate of individual tags enables tagging programs to be more flexible in the release of tags. Previous multi-year tagging models required releases to be aggregated to a single release period during a specific tagging event (i.e. mean day of all releases for a tagging event). The new model allows for tagging projects to be more flexible in their design and incorporate tags released at any time. This would allow for inclusion of tagged animals released by fishers throughout the fishing season (e.g. berried female lobsters). The ‘exact time’ model also enabled finer scale (weeks, months etc) estimates of catchability to be estimated in addition to mortality rates, thus increasing the information obtained from a tagging study.
 
Final Report • 2017-09-29
2003-051-DLD.pdf

Summary

Tagging is an important tool for estimating key fisheries parameters such as fishing mortality, natural mortality and growth. This project identified the need for future tagging projects to undertake preliminary studies to determine the impact of tagging on both growth and survival, and we developed a new method for obtaining in situ measurements. While aquaria studies have demonstrated that the timing of tagging in relation to the lobster moult cycle can have an impact on tag-induced mortality, these studies estimated that the impacts were low. The in situ method in our study found similar moult cycle impacts but our impact estimates were substantially higher than previously considered.
 
New tagging projects for lobster should evaluate the use of PIT tags as this project demonstrated the ‘proof of concept’ in obtaining a 100% tag reporting rate by scanners placed at strategic locations on board fishing vessels. With as few as 10% of the fleet having scanners, PIT tagging proved to be cost beneficial compared to conventional T-bar tags. As PIT tags are normally imbedded in the muscle of an animal, they are ‘invisible’ to potential reporters (e.g. fishers). A hybrid T-bar tag developed and tested in this project combined a T-bar tag and a PIT tag so that the PIT tag remained visible to fishers for reporting on vessels that did not contain scanners. An additional benefit of the hybrid tag was that it removed the potential for the PIT tag to be ingested.
 
The development of an ‘exact time’ survival model that followed the fate of individual tags enables tagging programs to be more flexible in the release of tags. Previous multi-year tagging models required releases to be aggregated to a single release period during a specific tagging event (i.e. mean day of all releases for a tagging event). The new model allows for tagging projects to be more flexible in their design and incorporate tags released at any time. This would allow for inclusion of tagged animals released by fishers throughout the fishing season (e.g. berried female lobsters). The ‘exact time’ model also enabled finer scale (weeks, months etc) estimates of catchability to be estimated in addition to mortality rates, thus increasing the information obtained from a tagging study.
 
Final Report • 2017-09-29
2003-051-DLD.pdf

Summary

Tagging is an important tool for estimating key fisheries parameters such as fishing mortality, natural mortality and growth. This project identified the need for future tagging projects to undertake preliminary studies to determine the impact of tagging on both growth and survival, and we developed a new method for obtaining in situ measurements. While aquaria studies have demonstrated that the timing of tagging in relation to the lobster moult cycle can have an impact on tag-induced mortality, these studies estimated that the impacts were low. The in situ method in our study found similar moult cycle impacts but our impact estimates were substantially higher than previously considered.
 
New tagging projects for lobster should evaluate the use of PIT tags as this project demonstrated the ‘proof of concept’ in obtaining a 100% tag reporting rate by scanners placed at strategic locations on board fishing vessels. With as few as 10% of the fleet having scanners, PIT tagging proved to be cost beneficial compared to conventional T-bar tags. As PIT tags are normally imbedded in the muscle of an animal, they are ‘invisible’ to potential reporters (e.g. fishers). A hybrid T-bar tag developed and tested in this project combined a T-bar tag and a PIT tag so that the PIT tag remained visible to fishers for reporting on vessels that did not contain scanners. An additional benefit of the hybrid tag was that it removed the potential for the PIT tag to be ingested.
 
The development of an ‘exact time’ survival model that followed the fate of individual tags enables tagging programs to be more flexible in the release of tags. Previous multi-year tagging models required releases to be aggregated to a single release period during a specific tagging event (i.e. mean day of all releases for a tagging event). The new model allows for tagging projects to be more flexible in their design and incorporate tags released at any time. This would allow for inclusion of tagged animals released by fishers throughout the fishing season (e.g. berried female lobsters). The ‘exact time’ model also enabled finer scale (weeks, months etc) estimates of catchability to be estimated in addition to mortality rates, thus increasing the information obtained from a tagging study.
 
Final Report • 2017-09-29
2003-051-DLD.pdf

Summary

Tagging is an important tool for estimating key fisheries parameters such as fishing mortality, natural mortality and growth. This project identified the need for future tagging projects to undertake preliminary studies to determine the impact of tagging on both growth and survival, and we developed a new method for obtaining in situ measurements. While aquaria studies have demonstrated that the timing of tagging in relation to the lobster moult cycle can have an impact on tag-induced mortality, these studies estimated that the impacts were low. The in situ method in our study found similar moult cycle impacts but our impact estimates were substantially higher than previously considered.
 
New tagging projects for lobster should evaluate the use of PIT tags as this project demonstrated the ‘proof of concept’ in obtaining a 100% tag reporting rate by scanners placed at strategic locations on board fishing vessels. With as few as 10% of the fleet having scanners, PIT tagging proved to be cost beneficial compared to conventional T-bar tags. As PIT tags are normally imbedded in the muscle of an animal, they are ‘invisible’ to potential reporters (e.g. fishers). A hybrid T-bar tag developed and tested in this project combined a T-bar tag and a PIT tag so that the PIT tag remained visible to fishers for reporting on vessels that did not contain scanners. An additional benefit of the hybrid tag was that it removed the potential for the PIT tag to be ingested.
 
The development of an ‘exact time’ survival model that followed the fate of individual tags enables tagging programs to be more flexible in the release of tags. Previous multi-year tagging models required releases to be aggregated to a single release period during a specific tagging event (i.e. mean day of all releases for a tagging event). The new model allows for tagging projects to be more flexible in their design and incorporate tags released at any time. This would allow for inclusion of tagged animals released by fishers throughout the fishing season (e.g. berried female lobsters). The ‘exact time’ model also enabled finer scale (weeks, months etc) estimates of catchability to be estimated in addition to mortality rates, thus increasing the information obtained from a tagging study.
 

Estimation of gross value of fisheries production

Project number: 1998-166
Project Status:
Completed
Budget expenditure: $98,085.00
Principal Investigator: Deborah Brown
Organisation: Department of Agriculture, Fisheries and Forestry (DAFF) ABARES
Project start/end date: 28 Jun 1998 - 27 Sep 2001
Contact:
FRDC

Need

The development of statistics on Australian fisheries production and gross value of production (GVP) is required to meet a wide rang of demands.

First: GVP for specific fisheries are required for determining research and development levies for Fisheries Research and Development Corporation (FRDC) and Fish Resources Research Fund (FRRF) and for determining industry contributions to research. Because the estimates form the basis for research levies for each fishery, it is important for the system to be independent from those involved in the management and marketing processes to ensure the neutrality and integrity of the esimates.

Second:The data is extensively used by the fishing ndustry and by providers of services to the fishing indusry (such as banks) in making investment decisions and in longer term planning of marketing stategies. The importance of the information provided by this project was highlighted at the 1997 FRDC Australian Fisheries Economics Statistics Workshop, and has been reafirmed by the Fisheries Economic Statistics Steering Committee.

Third: the existences of these data in a readily accessible form provides the basis for a range of other activities, including the setting of research priorities by fisheries managers, industry and research organisations and the selection of a research portfolio by funding agencies. The project data are used to meet Australia's obligations to provide fisheries information to international organisations, such as FAO and OECD, a task which was handed over to ABARE under the FRRF arrangements and for which support has been provided under FRRF.

Fourth: there are significant economies in centralising the GVP data project. In the absence of this project the workload of a range of organisaions involved in Commonwealth fisheries management would be substantially increased to dealwith public, industry and government enquiries. This inturn, woud result inan increase in the costs of fisheries management and admiistration.

Fifth: the costs of administration of fisheries research would be similarly affected. The current arrangements for the allocation of fisheries research funding and for determining research priorities could not be feasibly undertaken in the absence of the project.

Objectives

1. To develop and maintain a data base of producion, value and trade statisitcs for the Australian fishing industry, including aquaculture.

Final report

Author: Deborah Brown
Final Report • 2001-06-22 • 615.51 KB
1998-166-DLD.pdf

Summary

To meet the needs of the fishing industry and fisheries managers, policy makers and researchers, ABARE has been publishing on an annual basis, detailed production and trade data in Australian Fisheries Statistics since 1991. The research undertaken in this project (98/166) produced data on the volume and value of production from state and Commonwealth fisheries, and the volume and value of Australian fisheries trade, by destination, source and product, covering the years 1995-96 to 1999-2000. These reports also contain industry structure profiles of Commonwealth and state fisheries. 

An important part of this project was the requirement to implement a process of continuous improvement over the life of the project. These improvements were aimed at enhancing the coverage of fisheries, so all commercial fishing activities were included, maintaining the relevance of the data presented in both the production and trade tables, and implement processes so that the valuation of commercial fishing was undertaken in a consistent framework.

Final Report • 2001-06-22 • 615.51 KB
1998-166-DLD.pdf

Summary

To meet the needs of the fishing industry and fisheries managers, policy makers and researchers, ABARE has been publishing on an annual basis, detailed production and trade data in Australian Fisheries Statistics since 1991. The research undertaken in this project (98/166) produced data on the volume and value of production from state and Commonwealth fisheries, and the volume and value of Australian fisheries trade, by destination, source and product, covering the years 1995-96 to 1999-2000. These reports also contain industry structure profiles of Commonwealth and state fisheries. 

An important part of this project was the requirement to implement a process of continuous improvement over the life of the project. These improvements were aimed at enhancing the coverage of fisheries, so all commercial fishing activities were included, maintaining the relevance of the data presented in both the production and trade tables, and implement processes so that the valuation of commercial fishing was undertaken in a consistent framework.

Final Report • 2001-06-22 • 615.51 KB
1998-166-DLD.pdf

Summary

To meet the needs of the fishing industry and fisheries managers, policy makers and researchers, ABARE has been publishing on an annual basis, detailed production and trade data in Australian Fisheries Statistics since 1991. The research undertaken in this project (98/166) produced data on the volume and value of production from state and Commonwealth fisheries, and the volume and value of Australian fisheries trade, by destination, source and product, covering the years 1995-96 to 1999-2000. These reports also contain industry structure profiles of Commonwealth and state fisheries. 

An important part of this project was the requirement to implement a process of continuous improvement over the life of the project. These improvements were aimed at enhancing the coverage of fisheries, so all commercial fishing activities were included, maintaining the relevance of the data presented in both the production and trade tables, and implement processes so that the valuation of commercial fishing was undertaken in a consistent framework.

Final Report • 2001-06-22 • 615.51 KB
1998-166-DLD.pdf

Summary

To meet the needs of the fishing industry and fisheries managers, policy makers and researchers, ABARE has been publishing on an annual basis, detailed production and trade data in Australian Fisheries Statistics since 1991. The research undertaken in this project (98/166) produced data on the volume and value of production from state and Commonwealth fisheries, and the volume and value of Australian fisheries trade, by destination, source and product, covering the years 1995-96 to 1999-2000. These reports also contain industry structure profiles of Commonwealth and state fisheries. 

An important part of this project was the requirement to implement a process of continuous improvement over the life of the project. These improvements were aimed at enhancing the coverage of fisheries, so all commercial fishing activities were included, maintaining the relevance of the data presented in both the production and trade tables, and implement processes so that the valuation of commercial fishing was undertaken in a consistent framework.

Final Report • 2001-06-22 • 615.51 KB
1998-166-DLD.pdf

Summary

To meet the needs of the fishing industry and fisheries managers, policy makers and researchers, ABARE has been publishing on an annual basis, detailed production and trade data in Australian Fisheries Statistics since 1991. The research undertaken in this project (98/166) produced data on the volume and value of production from state and Commonwealth fisheries, and the volume and value of Australian fisheries trade, by destination, source and product, covering the years 1995-96 to 1999-2000. These reports also contain industry structure profiles of Commonwealth and state fisheries. 

An important part of this project was the requirement to implement a process of continuous improvement over the life of the project. These improvements were aimed at enhancing the coverage of fisheries, so all commercial fishing activities were included, maintaining the relevance of the data presented in both the production and trade tables, and implement processes so that the valuation of commercial fishing was undertaken in a consistent framework.

Development of an individual transferable catch quota model for the Coral Reef Fin Fish Fishery of the Great Barrier Reef

Project number: 2004-030
Project Status:
Completed
Budget expenditure: $476,940.00
Principal Investigator: Richard Little
Organisation: James Cook University (JCU)
Project start/end date: 14 Jan 2005 - 29 Oct 2008
Contact:
FRDC

Need

One of the major research priorities of QFIRAC, REEFMAC, QFS, GBRMPA, and other fisheries' stakeholders of the GBR concerns the need to develop innovative approaches for determining the sustainability of the fisheries for the exploited reef fish species, particularly the major target species of the GBR Coral Reef Fin Fish Fishery, common coral trout and red throat emperor. This need has become even more pronounced with the recent release of the management plan for the fishery, which is largely dependent upon an Individual Transferable catch Quota (ITQ) system and the impending GBRMPA Representative Areas Program (RAP). A model involving complex effort dynamics associated with an extensive system of "no-take" areas and a significant recreational harvest (e.g., unlike the SE Trawl Fishery) that provides a framework for setting appropriate Total Allowable Catches (TACs) and evaluating their impacts has yet to be developed.

This proposal, therefore, arose in response to major concerns for the sustainability of the GBR Coral Reef Fin Fish Fishery. It addresses directly QFIRAC's key R&D priorities in sustainability assessments by developing innovative assessment methodologies, sustainability indicators for target species in commercial fisheries, and using a Management Strategy Evaluation (MSE) approach. The "standard" approach to providing management advice for fisheries managed using ITQs involves, for each target species, fitting a population dynamics model to data collected for large geographic areas and calculating catch limits according to pre-specific decision rules (such as F0.1). However, this approach is likely to fail to achieve the management objectives for the GBR Coral Reef Fin Fish Fishery because it ignores spatial heterogeneity in population structure and the multi-species and multi-sector nature of the fishery. Also, the data typically required to apply these methods is not available for the GBR Coral Reef Fin Fish Fishery. In addition, little is known about the bioeconomic impacts and sophisticated effort dynamics associated with an ITQ managed multi-species, multi-sector fishery such as the GBR Coral Reef Fin Fish Fishery.

Consequently, we propose to extend the MSE framework developed as part of the CRC Reef Effects of Line Fishing (ELF) Project and other related FRDC funded projects (1997-124, 1998-131, 2001-020). Results from this project will inform stakeholders and decision makers about the bioeconomic trade-offs associated with a variety of alternative rules for setting TACs. This is exactly the type of information required as the basis for the selection of monitoring strategies and decision rules. This project, therefore, will provide a management tool by which appropriate TACs can be evaluated given alternate harvest strategies related to effort displacement caused by the RAP and the significant recreational harvest.

Objectives

1. To extend the existing MSE framework for the GBR Coral Reef Fin Fish Fishery so that management controls evaluated can include catch limits implemented as Individual Transferable Quotas.
2. To evaluate the likely effects on the sustainability of common coral trout and red throat emperor of regional shifts in catch distributions in response to spatial closures and potential displacement of fishing effort associated with the GBRMPA Representative Areas Program.
3. To evaluate alternative management strategies for common coral trout and red throat emperor in the Coral Reef Fin Fish Fishery of the Great Barrier Reef in terms of the trade-offs among the objectives of the commercial, recreational and charter fisheries.

Final report

ISBN: 9.78E+12
Author: Richard Little

Development of the tools for long term management of the giant crab resource: data collection methodology, stock assessment and harvest strategy evaluation

Project number: 2001-042
Project Status:
Completed
Budget expenditure: $246,572.00
Principal Investigator: Caleb Gardner
Organisation: University of Tasmania (UTAS)
Project start/end date: 29 Jun 2001 - 31 Mar 2008
Contact:
FRDC
SPECIES

Need

The ability to conduct stock assessments of the giant crab resource and to evaluate management strategies is fundamental for sustainable development of this resource.

Stock assessment of giant crabs across southern Australia is not formalised although this is a requirement for state management and is also required to meet Federal expectations on export of wildlife under Schedule 4 of the Wildlife Protection Act. Our ability to conduct assessments is limited by the data and analytical tools that are available.

Agencies involved in managing giant crabs require information on the setting of meaningful fishery performance indicators, and they also require ongoing information collection to evaluate these indicators. It is important to have the ability to track changes in biomass (or an index of biomass), recruitment of sized animals into the fishery, and reproductive output. Managers require information to balance the goals of optimising yields and ensuring adequate reproductive output is maintained.

Regardless of the management system implemented, all States require the ability to evaluate different harvest strategies such as the impact of closed seasons, different size limits and different TACs. While egg and yield per recruit analyses have been completed, there is a need for information to set TACs using best available knowledge on the state of the fishery.

An over-riding need for assessment of giant crab fisheries is that it be low cost. This is not a high value fishery and biologists conducting future assessments will have access to only low levels of funding. Placing observers on board vessels is not cost effective for the long term. Future assessments will be reliant on commercial log book data and on industry data collection programs to be developed through this proposal.

Objectives

1. To develop a low cost, long term, giant crab resource assessment and data collection methodology.
2. To quantify biases in the historical log book data to increase its value for resource assessments.
3. To obtain industry's understanding/observations of basic biological and market processes (eg. moulting, egg-bearing, mating, migration, beach prices influences) and how their fishing practices are adapted to this knowledge (eg. targeting of size classes, seasonality of effort, etc.).
4. To develop the ability to investigate alternative harvest strategies (sustainability of different TACs
closed seasons etc.).

Final report

ISBN: 9781862954311
Author: Caleb Gardner
Final Report • 2008-03-31 • 10.86 MB
2001-042-DLD.pdf

Summary

The project has developed tools for low cost assessment of the giant crab resource across southern Australia.  

Stock assessment and management response is now increasingly based on biomass estimates from this project.  Risk of poor management decisions is thus reduced, which contributes to greater business certainty.  

This project was constructed with the awareness that the resource was small and the fishery would have little ability to fund expensive data collection systems in the future, beyond catch rate data from logbooks.  Size structure data from the fishery was considered the main data type to be valuable for ongoing assessment, but also expensive to collect.  Fishers have adopted electronic calipers combined with an electronic data logger, the solution developed in this project.  This system has dispensed with paper records so that work at sea is easier, and costs for data management (e.g. data entry) are reduced.

Specialised software was developed for conducting model runs to facilitate altering parameters, running a range of alternative scenarios, and plotting outcomes.

Giant crab stock assessments are utilizing outputs from this model.  The fishery performance indicators in Tasmania are being re-written in a new management plan to formalize the adoption of the model outputs.   

Keywords: giant crab, Pseudocarcinus gigas, harvest strategy, population model, data collection.

Final Report • 2008-03-31 • 10.86 MB
2001-042-DLD.pdf

Summary

The project has developed tools for low cost assessment of the giant crab resource across southern Australia.  

Stock assessment and management response is now increasingly based on biomass estimates from this project.  Risk of poor management decisions is thus reduced, which contributes to greater business certainty.  

This project was constructed with the awareness that the resource was small and the fishery would have little ability to fund expensive data collection systems in the future, beyond catch rate data from logbooks.  Size structure data from the fishery was considered the main data type to be valuable for ongoing assessment, but also expensive to collect.  Fishers have adopted electronic calipers combined with an electronic data logger, the solution developed in this project.  This system has dispensed with paper records so that work at sea is easier, and costs for data management (e.g. data entry) are reduced.

Specialised software was developed for conducting model runs to facilitate altering parameters, running a range of alternative scenarios, and plotting outcomes.

Giant crab stock assessments are utilizing outputs from this model.  The fishery performance indicators in Tasmania are being re-written in a new management plan to formalize the adoption of the model outputs.   

Keywords: giant crab, Pseudocarcinus gigas, harvest strategy, population model, data collection.

Final Report • 2008-03-31 • 10.86 MB
2001-042-DLD.pdf

Summary

The project has developed tools for low cost assessment of the giant crab resource across southern Australia.  

Stock assessment and management response is now increasingly based on biomass estimates from this project.  Risk of poor management decisions is thus reduced, which contributes to greater business certainty.  

This project was constructed with the awareness that the resource was small and the fishery would have little ability to fund expensive data collection systems in the future, beyond catch rate data from logbooks.  Size structure data from the fishery was considered the main data type to be valuable for ongoing assessment, but also expensive to collect.  Fishers have adopted electronic calipers combined with an electronic data logger, the solution developed in this project.  This system has dispensed with paper records so that work at sea is easier, and costs for data management (e.g. data entry) are reduced.

Specialised software was developed for conducting model runs to facilitate altering parameters, running a range of alternative scenarios, and plotting outcomes.

Giant crab stock assessments are utilizing outputs from this model.  The fishery performance indicators in Tasmania are being re-written in a new management plan to formalize the adoption of the model outputs.   

Keywords: giant crab, Pseudocarcinus gigas, harvest strategy, population model, data collection.

Final Report • 2008-03-31 • 10.86 MB
2001-042-DLD.pdf

Summary

The project has developed tools for low cost assessment of the giant crab resource across southern Australia.  

Stock assessment and management response is now increasingly based on biomass estimates from this project.  Risk of poor management decisions is thus reduced, which contributes to greater business certainty.  

This project was constructed with the awareness that the resource was small and the fishery would have little ability to fund expensive data collection systems in the future, beyond catch rate data from logbooks.  Size structure data from the fishery was considered the main data type to be valuable for ongoing assessment, but also expensive to collect.  Fishers have adopted electronic calipers combined with an electronic data logger, the solution developed in this project.  This system has dispensed with paper records so that work at sea is easier, and costs for data management (e.g. data entry) are reduced.

Specialised software was developed for conducting model runs to facilitate altering parameters, running a range of alternative scenarios, and plotting outcomes.

Giant crab stock assessments are utilizing outputs from this model.  The fishery performance indicators in Tasmania are being re-written in a new management plan to formalize the adoption of the model outputs.   

Keywords: giant crab, Pseudocarcinus gigas, harvest strategy, population model, data collection.

Final Report • 2008-03-31 • 10.86 MB
2001-042-DLD.pdf

Summary

The project has developed tools for low cost assessment of the giant crab resource across southern Australia.  

Stock assessment and management response is now increasingly based on biomass estimates from this project.  Risk of poor management decisions is thus reduced, which contributes to greater business certainty.  

This project was constructed with the awareness that the resource was small and the fishery would have little ability to fund expensive data collection systems in the future, beyond catch rate data from logbooks.  Size structure data from the fishery was considered the main data type to be valuable for ongoing assessment, but also expensive to collect.  Fishers have adopted electronic calipers combined with an electronic data logger, the solution developed in this project.  This system has dispensed with paper records so that work at sea is easier, and costs for data management (e.g. data entry) are reduced.

Specialised software was developed for conducting model runs to facilitate altering parameters, running a range of alternative scenarios, and plotting outcomes.

Giant crab stock assessments are utilizing outputs from this model.  The fishery performance indicators in Tasmania are being re-written in a new management plan to formalize the adoption of the model outputs.   

Keywords: giant crab, Pseudocarcinus gigas, harvest strategy, population model, data collection.

Development of a northern Australian squid fishery

Project number: 1994-017
Project Status:
Completed
Budget expenditure: $154,668.33
Principal Investigator: Malcolm Dunning
Organisation: Department of Primary Industries (QLD)
Project start/end date: 27 Jun 1994 - 30 Jun 2001
Contact:
FRDC

Objectives

1. To document the known distribution and seasonal abundance of squid (loligo spp.) and northern calamary (Sepioteuthis)
2. To investigate species composition, seasonal size composition and basic life history characteristics of existing and potentially commercially important northern Australian squid resources
3. To undertake gear assessment/experimental fishing for squid using jigs under lights, lift nets and purpose designed squid trawls off southern and central Queensland in collaboration with commercial fishers
4. To assess the relative seasonal catch rates of squid at selected locations off southern and central Queensland in collaboration with commercial fishers

Final report

Author: Malcolm Dunning Kate Yeomans Scott McKinnon
Final Report • 2000-11-08 • 3.62 MB
1994-017-DLD.pdf

Summary

Squid are an increasing component in the reported byproduct of commercial prawn and finfish trawlers in northern Australian shelf waters and interest has been shown by Queensland and Northern Territory fishers in developing target fisheries for squid using jigs. In general, squid caught on jigs or in lift or other surround nets are of higher quality, larger size and, on overseas markets, fetch a much higher price than squid caught by trawling.

In support of developing squid jig fisheries and to provide management advice, this project aimed to consolidate and enhance our knowledge of their fisheries biology and suitable fishing methods for inshore squid in northern Australian waters.

Keywords: inshore squid, developmental fisheries, jigging, tropical Australia, Loliginidae, Photololigo, Sepioteuthis

Project products

Guide • 3.74 MB
1994-017 Field guide to Australian cephalopods.pdf

Summary

The aim of this guide is to help commercial fishers, scientific observers and recreational fishermen to identify the most common cephalopods (cuttlefish, squid and octopus) caught in Australian fisheries. Logbooks kept by commercial and recreational fishers provide essential information for fisheries research and management; however, for the records to be useful the catch must be correctly identified, especially in any developing fishery.

Cephalopods, particularly squid, occur in commercial quantities throughout the Australian Fishing Zone but remain largely under utilized. Squid are highly productive species, and generally live for less than a year. They are caught throughout the year, usually with high catches in spring and summer. High catch rates have been recorded in targeted cephalopod trawl fisheries off northern Australia.

Many of the species treated here have not been described and illustrated in the literature, and until now there has been no shipboard guide to the local Australian cephalopods of commercial importance. However, some of the species are included in other publications, some of which are in the bibliography.

As Australia's cephalopod fisheries develop to the stage where management plans are required, the composition, size and sustainable harvest levels of the stocks must be assessed. Commonwealth-managed fisheries are evaluated on the basis of this information. At present, recorded landings represent only a fraction of the cephalopod catch, as cephalopods taken as bycatch are often discarded at sea or used as bait in other fisheries.

Final Report • 2000-11-08 • 3.62 MB
1994-017-DLD.pdf

Summary

Squid are an increasing component in the reported byproduct of commercial prawn and finfish trawlers in northern Australian shelf waters and interest has been shown by Queensland and Northern Territory fishers in developing target fisheries for squid using jigs. In general, squid caught on jigs or in lift or other surround nets are of higher quality, larger size and, on overseas markets, fetch a much higher price than squid caught by trawling.

In support of developing squid jig fisheries and to provide management advice, this project aimed to consolidate and enhance our knowledge of their fisheries biology and suitable fishing methods for inshore squid in northern Australian waters.

Keywords: inshore squid, developmental fisheries, jigging, tropical Australia, Loliginidae, Photololigo, Sepioteuthis

Guide • 3.74 MB
1994-017 Field guide to Australian cephalopods.pdf

Summary

The aim of this guide is to help commercial fishers, scientific observers and recreational fishermen to identify the most common cephalopods (cuttlefish, squid and octopus) caught in Australian fisheries. Logbooks kept by commercial and recreational fishers provide essential information for fisheries research and management; however, for the records to be useful the catch must be correctly identified, especially in any developing fishery.

Cephalopods, particularly squid, occur in commercial quantities throughout the Australian Fishing Zone but remain largely under utilized. Squid are highly productive species, and generally live for less than a year. They are caught throughout the year, usually with high catches in spring and summer. High catch rates have been recorded in targeted cephalopod trawl fisheries off northern Australia.

Many of the species treated here have not been described and illustrated in the literature, and until now there has been no shipboard guide to the local Australian cephalopods of commercial importance. However, some of the species are included in other publications, some of which are in the bibliography.

As Australia's cephalopod fisheries develop to the stage where management plans are required, the composition, size and sustainable harvest levels of the stocks must be assessed. Commonwealth-managed fisheries are evaluated on the basis of this information. At present, recorded landings represent only a fraction of the cephalopod catch, as cephalopods taken as bycatch are often discarded at sea or used as bait in other fisheries.

Final Report • 2000-11-08 • 3.62 MB
1994-017-DLD.pdf

Summary

Squid are an increasing component in the reported byproduct of commercial prawn and finfish trawlers in northern Australian shelf waters and interest has been shown by Queensland and Northern Territory fishers in developing target fisheries for squid using jigs. In general, squid caught on jigs or in lift or other surround nets are of higher quality, larger size and, on overseas markets, fetch a much higher price than squid caught by trawling.

In support of developing squid jig fisheries and to provide management advice, this project aimed to consolidate and enhance our knowledge of their fisheries biology and suitable fishing methods for inshore squid in northern Australian waters.

Keywords: inshore squid, developmental fisheries, jigging, tropical Australia, Loliginidae, Photololigo, Sepioteuthis

Guide • 3.74 MB
1994-017 Field guide to Australian cephalopods.pdf

Summary

The aim of this guide is to help commercial fishers, scientific observers and recreational fishermen to identify the most common cephalopods (cuttlefish, squid and octopus) caught in Australian fisheries. Logbooks kept by commercial and recreational fishers provide essential information for fisheries research and management; however, for the records to be useful the catch must be correctly identified, especially in any developing fishery.

Cephalopods, particularly squid, occur in commercial quantities throughout the Australian Fishing Zone but remain largely under utilized. Squid are highly productive species, and generally live for less than a year. They are caught throughout the year, usually with high catches in spring and summer. High catch rates have been recorded in targeted cephalopod trawl fisheries off northern Australia.

Many of the species treated here have not been described and illustrated in the literature, and until now there has been no shipboard guide to the local Australian cephalopods of commercial importance. However, some of the species are included in other publications, some of which are in the bibliography.

As Australia's cephalopod fisheries develop to the stage where management plans are required, the composition, size and sustainable harvest levels of the stocks must be assessed. Commonwealth-managed fisheries are evaluated on the basis of this information. At present, recorded landings represent only a fraction of the cephalopod catch, as cephalopods taken as bycatch are often discarded at sea or used as bait in other fisheries.

Final Report • 2000-11-08 • 3.62 MB
1994-017-DLD.pdf

Summary

Squid are an increasing component in the reported byproduct of commercial prawn and finfish trawlers in northern Australian shelf waters and interest has been shown by Queensland and Northern Territory fishers in developing target fisheries for squid using jigs. In general, squid caught on jigs or in lift or other surround nets are of higher quality, larger size and, on overseas markets, fetch a much higher price than squid caught by trawling.

In support of developing squid jig fisheries and to provide management advice, this project aimed to consolidate and enhance our knowledge of their fisheries biology and suitable fishing methods for inshore squid in northern Australian waters.

Keywords: inshore squid, developmental fisheries, jigging, tropical Australia, Loliginidae, Photololigo, Sepioteuthis

Guide • 3.74 MB
1994-017 Field guide to Australian cephalopods.pdf

Summary

The aim of this guide is to help commercial fishers, scientific observers and recreational fishermen to identify the most common cephalopods (cuttlefish, squid and octopus) caught in Australian fisheries. Logbooks kept by commercial and recreational fishers provide essential information for fisheries research and management; however, for the records to be useful the catch must be correctly identified, especially in any developing fishery.

Cephalopods, particularly squid, occur in commercial quantities throughout the Australian Fishing Zone but remain largely under utilized. Squid are highly productive species, and generally live for less than a year. They are caught throughout the year, usually with high catches in spring and summer. High catch rates have been recorded in targeted cephalopod trawl fisheries off northern Australia.

Many of the species treated here have not been described and illustrated in the literature, and until now there has been no shipboard guide to the local Australian cephalopods of commercial importance. However, some of the species are included in other publications, some of which are in the bibliography.

As Australia's cephalopod fisheries develop to the stage where management plans are required, the composition, size and sustainable harvest levels of the stocks must be assessed. Commonwealth-managed fisheries are evaluated on the basis of this information. At present, recorded landings represent only a fraction of the cephalopod catch, as cephalopods taken as bycatch are often discarded at sea or used as bait in other fisheries.

Final Report • 2000-11-08 • 3.62 MB
1994-017-DLD.pdf

Summary

Squid are an increasing component in the reported byproduct of commercial prawn and finfish trawlers in northern Australian shelf waters and interest has been shown by Queensland and Northern Territory fishers in developing target fisheries for squid using jigs. In general, squid caught on jigs or in lift or other surround nets are of higher quality, larger size and, on overseas markets, fetch a much higher price than squid caught by trawling.

In support of developing squid jig fisheries and to provide management advice, this project aimed to consolidate and enhance our knowledge of their fisheries biology and suitable fishing methods for inshore squid in northern Australian waters.

Keywords: inshore squid, developmental fisheries, jigging, tropical Australia, Loliginidae, Photololigo, Sepioteuthis

Guide • 3.74 MB
1994-017 Field guide to Australian cephalopods.pdf

Summary

The aim of this guide is to help commercial fishers, scientific observers and recreational fishermen to identify the most common cephalopods (cuttlefish, squid and octopus) caught in Australian fisheries. Logbooks kept by commercial and recreational fishers provide essential information for fisheries research and management; however, for the records to be useful the catch must be correctly identified, especially in any developing fishery.

Cephalopods, particularly squid, occur in commercial quantities throughout the Australian Fishing Zone but remain largely under utilized. Squid are highly productive species, and generally live for less than a year. They are caught throughout the year, usually with high catches in spring and summer. High catch rates have been recorded in targeted cephalopod trawl fisheries off northern Australia.

Many of the species treated here have not been described and illustrated in the literature, and until now there has been no shipboard guide to the local Australian cephalopods of commercial importance. However, some of the species are included in other publications, some of which are in the bibliography.

As Australia's cephalopod fisheries develop to the stage where management plans are required, the composition, size and sustainable harvest levels of the stocks must be assessed. Commonwealth-managed fisheries are evaluated on the basis of this information. At present, recorded landings represent only a fraction of the cephalopod catch, as cephalopods taken as bycatch are often discarded at sea or used as bait in other fisheries.

Further Development of an Employment Web Page for the Western Rocklobster Industry

Project number: 2007-307
Project Status:
Completed
Budget expenditure: $27,550.00
Principal Investigator: Dexter Davies
Organisation: Western Rock Lobster Council Inc (WRLC)
Project start/end date: 27 Feb 2007 - 30 Jun 2008
Contact:
FRDC

Need

The industry is facing a labour shortage, with many crew opting to work in the mining sector for significantly higher returns than are available from the fishing industry. This results in skilled crew moving away from the fishing industry, with labour shortages being filled by inexperienced crew which leads to safety implications, a high crew turn over, and less efficient fishing operations. Consequently, fishers are looking for ways to find skilled crew, in a timely, cost effective manner, to reduce down-time resulting from crew shortages.

The current cost-price squeeze has an additional impact on fishing operations, as fishers are forced to spend more time advertising, training, and managing crew shortages at a time when many fishers are already facing significant income reductions. The WA Fishing Industry Council has also recognised the need to identify a career pathway for employees in the fishing industry to improve employment opportunities, and this web page program would assist with linking the career pathway with these employment opportunities in the fishing industry.

The employment web page project was initially funded by the Western Rocklobster Council, however funding to the Council has been decreased due to a reduction in the value of the GVP of the fishery, consequently, further funding is not available to projects outside of the core business of the Council under that revenue stream. This application will assist with providing the funds for increasing awareness and use of the web page by employment agencies, as well as technical support for updating the website to accommodate addition fisheries at a later date.

Objectives

1. Increased numbers of advertisements on the web page
2. Increased placings of crew with fishers looking for employees
3. Provide opportunities for training and employment agencies to network with the fishing industry for employment purposes
4. Identify the potential for using the JobSearch site to create a template for the wider fishing industry (feasibility study).

Development of sponge (Spongia Spp.) farming as a viable commercial enterprise for remote Aboriginal communities

Project number: 2001-225
Project Status:
Completed
Budget expenditure: $15,000.00
Principal Investigator: Graeme Dobson
Organisation: Charles Darwin University (CDU)
Project start/end date: 21 Jul 2001 - 30 Nov 2003
Contact:
FRDC

Need

There is an urgent need for employment and income generating projects within remote communities of northern Australia.

Despite there being several excellent sites for aquaculture near indigenous communities, there is currently no significant indigenous involvement in aquaculture in Northern Australia. This is partially the result of cultural norms in communities not being compatible with the intensive and high technology farming systems now in common use. There is a need to develop small-scale projects with a level of technology that will allow the participation of indigenous groups.

Such projects will form the basis for a diversified aquaculture industry in the NT which will be inclusive of both indigenous and non-indigenous groups in remote areas. Such projects have the capacity to generate income from a comparatively low investment and collectively form a significant export for the NT.

The proposed project will:
*meet a well-defined need and contribute to the public good.
*Form the basis for the development of a viable, community based aquaculture industry that will enhance the aquaculture industry of the NT and provide employment and income to remote communities.
*Provide a basis for future research into the establishment of appropriate sponge farming systems in the NT.
*Involve members of indigenous communities in the identification of options and related research
- direct involvement of community members will be a primary method of extension

Objectives

1. Determine commercially viable sponge species in Northern Territory waters.
2. Identify markets for bath/cosmetic sponges.
3. Complete an economic evaluation of potential sponge farming systems in the NT.

Final report

ISBN: 1-876248-85-8
Author: Graeme Dobson
Final Report • 2003-12-11 • 1.86 MB
2001-225-DLD.pdf

Summary

Sponges have been employed for thousands of years for a wide variety of purposes, most commonly for basic hygiene (bath/toilet sponges), padding (historically under armour and saddles) and in certain manufacturing processes. World production from the wild harvest has, however, declined significantly this century due to over fishing, pollution and disease in the traditional fisheries (Mediterranean and Caribbean). Concurrently with this decline the demand for natural sponges for domestic (many people prefer to use a natural product), industrial and medical purposes has risen.
 
Three commercially viable species of sponge have been identified in this report from Northern Territory waters. All three are found adjacent to indigenous homelands in Arnhem Land and are known to some of the inhabitants of the area. With the backing of Homeland Associations, several Traditional Owners have expressed a strong desire to pursue sponge farming as soon as practicable. The adoption of sponge farming would directly benefit the homelands by providing ‘real’ employment, financial return for effort and a reduction in dependence on government funding. Sponge farming also has very good potential to provide a valuable new export product for Northern Australia.
 
Sponge farming is environmentally friendly. Apart from the initial collection of parent stock, there is no appreciable impact on the environment from sponge farming. Once the farm is established all stock replacement is produced on the farm and there is no need for further wild collection. Sponges are non-polluting—they are nett users, rather than producers, of nutrients and also feed on bacteria from the water column. Sponges process hundreds of litres of water per hour and remove up 95% of nutrients and bacteria—this has created interest in using sponges to reduce the effluent being discharged into the sea by both humans and aquaculture farms.
 
Farmed sponges are propagated asexually. A mature sponge is cut into pieces approximately 2–3 cm square on each side, the pieces threaded onto a piece of thin rope, wire or bamboo and hung in the water to grow. Once the sponge is placed in the water it needs no further direct care until it is harvested. Sponges are self-cleaning and have few predators (except turtles in some places). Growth rates of sponges placed in the right environment are good, in Townsville the sponges grow to market size in 18 months – 2 years.
 
Identified markets for ‘bath’ and ‘cosmetic’ sponges are extremely buoyant. Over-fishing and disease have caused a severe downturn in production of sponges from traditional sponge fishing regions (the Mediterranean and Caribbean seas). This has left gaps in the market which have not been filled and are open to new producers. Sponges produced from pristine waters, such as those off North Australia, are likely to have a general marketing advantage over those from ‘polluted’ areas. In addition, sponges that can be labeled as being produced from aquaculture that is carried out by indigenous homeland communities will have a strong advantage in extensive niche markets, especially the tourist market.
 
Economically sponge farming appears to be well suited to remote areas. Sponge farms are inexpensive to set up ($13,500 including purchasing a suitable dinghy and motor) and operate ($3,000 per year). Experience in Micronesia shows that establishing and maintaining a farm of 30,000 sponges requires approximately 20–30 man hours per week. A farmer can expect a minimum return from a farm this size of $45,000 per year after four years. Niche markets available in Australia could mean that this return is at least double for Australian indigenous producers.
 
Final Report • 2003-12-11 • 1.86 MB
2001-225-DLD.pdf

Summary

Sponges have been employed for thousands of years for a wide variety of purposes, most commonly for basic hygiene (bath/toilet sponges), padding (historically under armour and saddles) and in certain manufacturing processes. World production from the wild harvest has, however, declined significantly this century due to over fishing, pollution and disease in the traditional fisheries (Mediterranean and Caribbean). Concurrently with this decline the demand for natural sponges for domestic (many people prefer to use a natural product), industrial and medical purposes has risen.
 
Three commercially viable species of sponge have been identified in this report from Northern Territory waters. All three are found adjacent to indigenous homelands in Arnhem Land and are known to some of the inhabitants of the area. With the backing of Homeland Associations, several Traditional Owners have expressed a strong desire to pursue sponge farming as soon as practicable. The adoption of sponge farming would directly benefit the homelands by providing ‘real’ employment, financial return for effort and a reduction in dependence on government funding. Sponge farming also has very good potential to provide a valuable new export product for Northern Australia.
 
Sponge farming is environmentally friendly. Apart from the initial collection of parent stock, there is no appreciable impact on the environment from sponge farming. Once the farm is established all stock replacement is produced on the farm and there is no need for further wild collection. Sponges are non-polluting—they are nett users, rather than producers, of nutrients and also feed on bacteria from the water column. Sponges process hundreds of litres of water per hour and remove up 95% of nutrients and bacteria—this has created interest in using sponges to reduce the effluent being discharged into the sea by both humans and aquaculture farms.
 
Farmed sponges are propagated asexually. A mature sponge is cut into pieces approximately 2–3 cm square on each side, the pieces threaded onto a piece of thin rope, wire or bamboo and hung in the water to grow. Once the sponge is placed in the water it needs no further direct care until it is harvested. Sponges are self-cleaning and have few predators (except turtles in some places). Growth rates of sponges placed in the right environment are good, in Townsville the sponges grow to market size in 18 months – 2 years.
 
Identified markets for ‘bath’ and ‘cosmetic’ sponges are extremely buoyant. Over-fishing and disease have caused a severe downturn in production of sponges from traditional sponge fishing regions (the Mediterranean and Caribbean seas). This has left gaps in the market which have not been filled and are open to new producers. Sponges produced from pristine waters, such as those off North Australia, are likely to have a general marketing advantage over those from ‘polluted’ areas. In addition, sponges that can be labeled as being produced from aquaculture that is carried out by indigenous homeland communities will have a strong advantage in extensive niche markets, especially the tourist market.
 
Economically sponge farming appears to be well suited to remote areas. Sponge farms are inexpensive to set up ($13,500 including purchasing a suitable dinghy and motor) and operate ($3,000 per year). Experience in Micronesia shows that establishing and maintaining a farm of 30,000 sponges requires approximately 20–30 man hours per week. A farmer can expect a minimum return from a farm this size of $45,000 per year after four years. Niche markets available in Australia could mean that this return is at least double for Australian indigenous producers.
 
Final Report • 2003-12-11 • 1.86 MB
2001-225-DLD.pdf

Summary

Sponges have been employed for thousands of years for a wide variety of purposes, most commonly for basic hygiene (bath/toilet sponges), padding (historically under armour and saddles) and in certain manufacturing processes. World production from the wild harvest has, however, declined significantly this century due to over fishing, pollution and disease in the traditional fisheries (Mediterranean and Caribbean). Concurrently with this decline the demand for natural sponges for domestic (many people prefer to use a natural product), industrial and medical purposes has risen.
 
Three commercially viable species of sponge have been identified in this report from Northern Territory waters. All three are found adjacent to indigenous homelands in Arnhem Land and are known to some of the inhabitants of the area. With the backing of Homeland Associations, several Traditional Owners have expressed a strong desire to pursue sponge farming as soon as practicable. The adoption of sponge farming would directly benefit the homelands by providing ‘real’ employment, financial return for effort and a reduction in dependence on government funding. Sponge farming also has very good potential to provide a valuable new export product for Northern Australia.
 
Sponge farming is environmentally friendly. Apart from the initial collection of parent stock, there is no appreciable impact on the environment from sponge farming. Once the farm is established all stock replacement is produced on the farm and there is no need for further wild collection. Sponges are non-polluting—they are nett users, rather than producers, of nutrients and also feed on bacteria from the water column. Sponges process hundreds of litres of water per hour and remove up 95% of nutrients and bacteria—this has created interest in using sponges to reduce the effluent being discharged into the sea by both humans and aquaculture farms.
 
Farmed sponges are propagated asexually. A mature sponge is cut into pieces approximately 2–3 cm square on each side, the pieces threaded onto a piece of thin rope, wire or bamboo and hung in the water to grow. Once the sponge is placed in the water it needs no further direct care until it is harvested. Sponges are self-cleaning and have few predators (except turtles in some places). Growth rates of sponges placed in the right environment are good, in Townsville the sponges grow to market size in 18 months – 2 years.
 
Identified markets for ‘bath’ and ‘cosmetic’ sponges are extremely buoyant. Over-fishing and disease have caused a severe downturn in production of sponges from traditional sponge fishing regions (the Mediterranean and Caribbean seas). This has left gaps in the market which have not been filled and are open to new producers. Sponges produced from pristine waters, such as those off North Australia, are likely to have a general marketing advantage over those from ‘polluted’ areas. In addition, sponges that can be labeled as being produced from aquaculture that is carried out by indigenous homeland communities will have a strong advantage in extensive niche markets, especially the tourist market.
 
Economically sponge farming appears to be well suited to remote areas. Sponge farms are inexpensive to set up ($13,500 including purchasing a suitable dinghy and motor) and operate ($3,000 per year). Experience in Micronesia shows that establishing and maintaining a farm of 30,000 sponges requires approximately 20–30 man hours per week. A farmer can expect a minimum return from a farm this size of $45,000 per year after four years. Niche markets available in Australia could mean that this return is at least double for Australian indigenous producers.
 
Final Report • 2003-12-11 • 1.86 MB
2001-225-DLD.pdf

Summary

Sponges have been employed for thousands of years for a wide variety of purposes, most commonly for basic hygiene (bath/toilet sponges), padding (historically under armour and saddles) and in certain manufacturing processes. World production from the wild harvest has, however, declined significantly this century due to over fishing, pollution and disease in the traditional fisheries (Mediterranean and Caribbean). Concurrently with this decline the demand for natural sponges for domestic (many people prefer to use a natural product), industrial and medical purposes has risen.
 
Three commercially viable species of sponge have been identified in this report from Northern Territory waters. All three are found adjacent to indigenous homelands in Arnhem Land and are known to some of the inhabitants of the area. With the backing of Homeland Associations, several Traditional Owners have expressed a strong desire to pursue sponge farming as soon as practicable. The adoption of sponge farming would directly benefit the homelands by providing ‘real’ employment, financial return for effort and a reduction in dependence on government funding. Sponge farming also has very good potential to provide a valuable new export product for Northern Australia.
 
Sponge farming is environmentally friendly. Apart from the initial collection of parent stock, there is no appreciable impact on the environment from sponge farming. Once the farm is established all stock replacement is produced on the farm and there is no need for further wild collection. Sponges are non-polluting—they are nett users, rather than producers, of nutrients and also feed on bacteria from the water column. Sponges process hundreds of litres of water per hour and remove up 95% of nutrients and bacteria—this has created interest in using sponges to reduce the effluent being discharged into the sea by both humans and aquaculture farms.
 
Farmed sponges are propagated asexually. A mature sponge is cut into pieces approximately 2–3 cm square on each side, the pieces threaded onto a piece of thin rope, wire or bamboo and hung in the water to grow. Once the sponge is placed in the water it needs no further direct care until it is harvested. Sponges are self-cleaning and have few predators (except turtles in some places). Growth rates of sponges placed in the right environment are good, in Townsville the sponges grow to market size in 18 months – 2 years.
 
Identified markets for ‘bath’ and ‘cosmetic’ sponges are extremely buoyant. Over-fishing and disease have caused a severe downturn in production of sponges from traditional sponge fishing regions (the Mediterranean and Caribbean seas). This has left gaps in the market which have not been filled and are open to new producers. Sponges produced from pristine waters, such as those off North Australia, are likely to have a general marketing advantage over those from ‘polluted’ areas. In addition, sponges that can be labeled as being produced from aquaculture that is carried out by indigenous homeland communities will have a strong advantage in extensive niche markets, especially the tourist market.
 
Economically sponge farming appears to be well suited to remote areas. Sponge farms are inexpensive to set up ($13,500 including purchasing a suitable dinghy and motor) and operate ($3,000 per year). Experience in Micronesia shows that establishing and maintaining a farm of 30,000 sponges requires approximately 20–30 man hours per week. A farmer can expect a minimum return from a farm this size of $45,000 per year after four years. Niche markets available in Australia could mean that this return is at least double for Australian indigenous producers.
 
Final Report • 2003-12-11 • 1.86 MB
2001-225-DLD.pdf

Summary

Sponges have been employed for thousands of years for a wide variety of purposes, most commonly for basic hygiene (bath/toilet sponges), padding (historically under armour and saddles) and in certain manufacturing processes. World production from the wild harvest has, however, declined significantly this century due to over fishing, pollution and disease in the traditional fisheries (Mediterranean and Caribbean). Concurrently with this decline the demand for natural sponges for domestic (many people prefer to use a natural product), industrial and medical purposes has risen.
 
Three commercially viable species of sponge have been identified in this report from Northern Territory waters. All three are found adjacent to indigenous homelands in Arnhem Land and are known to some of the inhabitants of the area. With the backing of Homeland Associations, several Traditional Owners have expressed a strong desire to pursue sponge farming as soon as practicable. The adoption of sponge farming would directly benefit the homelands by providing ‘real’ employment, financial return for effort and a reduction in dependence on government funding. Sponge farming also has very good potential to provide a valuable new export product for Northern Australia.
 
Sponge farming is environmentally friendly. Apart from the initial collection of parent stock, there is no appreciable impact on the environment from sponge farming. Once the farm is established all stock replacement is produced on the farm and there is no need for further wild collection. Sponges are non-polluting—they are nett users, rather than producers, of nutrients and also feed on bacteria from the water column. Sponges process hundreds of litres of water per hour and remove up 95% of nutrients and bacteria—this has created interest in using sponges to reduce the effluent being discharged into the sea by both humans and aquaculture farms.
 
Farmed sponges are propagated asexually. A mature sponge is cut into pieces approximately 2–3 cm square on each side, the pieces threaded onto a piece of thin rope, wire or bamboo and hung in the water to grow. Once the sponge is placed in the water it needs no further direct care until it is harvested. Sponges are self-cleaning and have few predators (except turtles in some places). Growth rates of sponges placed in the right environment are good, in Townsville the sponges grow to market size in 18 months – 2 years.
 
Identified markets for ‘bath’ and ‘cosmetic’ sponges are extremely buoyant. Over-fishing and disease have caused a severe downturn in production of sponges from traditional sponge fishing regions (the Mediterranean and Caribbean seas). This has left gaps in the market which have not been filled and are open to new producers. Sponges produced from pristine waters, such as those off North Australia, are likely to have a general marketing advantage over those from ‘polluted’ areas. In addition, sponges that can be labeled as being produced from aquaculture that is carried out by indigenous homeland communities will have a strong advantage in extensive niche markets, especially the tourist market.
 
Economically sponge farming appears to be well suited to remote areas. Sponge farms are inexpensive to set up ($13,500 including purchasing a suitable dinghy and motor) and operate ($3,000 per year). Experience in Micronesia shows that establishing and maintaining a farm of 30,000 sponges requires approximately 20–30 man hours per week. A farmer can expect a minimum return from a farm this size of $45,000 per year after four years. Niche markets available in Australia could mean that this return is at least double for Australian indigenous producers.
 

Arresting the decline of the commercial and recreational fisheries for mulloway (Argyrosomus japonicus)

Project number: 2002-005
Project Status:
Completed
Budget expenditure: $205,327.00
Principal Investigator: Charles A. Gray
Organisation: Department of Primary Industries and Regional Development (NSW)
Project start/end date: 29 Jun 2002 - 15 Mar 2006
Contact:
FRDC

Need

There is a need to synthesize all existing information and to obtain new basic biological and fisheries-related information on mulloway to be able to make informed management decisions concerning the continued sustainable harvesting of the species in NSW waters and elsewhere and to arrest the apparent decline in populations. Most importantly, the growth and age and reproductive biology of mulloway needs to be accurately described and data on the length, sex and age compositions of catches and how these vary between different fishing sectors and gear types needs to be collected and analyzed to provide us with even the most basic understanding of the potential effects of fishing on this very important species. Yield-per-recruit analyses need to be done to aid discussions on appropriate legal lengths.

Objectives

1. Synthesize, write and publish a review of the biology and fisheries of mulloway (and other relevant sciaenid species) in an international scientific journal and provide a layman’s summary that can be given to stakeholders.
2. Reanalyze all existing tagging information on mulloway.
3. Describe the growth and age and reproductive biology of mulloway in NSW and do yield-per-recruit analyses.
4. Determine the length, sex and age compositions of commercial catches of mulloway and assess how these vary between different gear types, industry sectors (e.g. estuary v ocean) and regionally.
5. Advise the commercial and recreational fishing communities and other interest groups on the biology of mulloway and provide recommendations on ways to stop the apparent decline in populations and future management and assessment strategies for the species.

Seafood CRC: improving profitability in the Western Rocklobster fishery using a rocklobster trap

Project number: 2008-900
Project Status:
Completed
Budget expenditure: $92,276.57
Principal Investigator: Dexter Davies
Organisation: Western Rock Lobster Council Inc (WRLC)
Project start/end date: 14 Nov 2008 - 14 Nov 2009
Contact:
FRDC

Need

For the WRL fishery, this situation has resulted primarily from a relatively static beach price for lobster and increasing fuel, labour and other input costs. A major driver for input costs in this fishery is the number of pot lifts, which is currently about 10 million annually, equating to a total cost of ~$60 million (average cost per potlift - $6.00). If a lobster trap could be introduced into this fishery with a volume approx twice that of traditional pots, thereby enabling fishers to capitalise on the gregarious nature of the animal whilst preventing escapees, the fishing behaviour of the fleet would adapt accordingly to focus on primarily extended soaks i.e. 48 and 72 hours. It is envisaged that the cost savings associated with this shift in fishing behaviour would translate to a more economically viable fleet.

The introduction of a lobster trap which causes a reduction in the number of pot lifts has the potential to enhance the primary measure of exploitation in the WRLF namely, catch per unit effort (CPUE). A 10-20% reduction in pot lifts over an entire season would result in cost savings to the tune of $6-12 million annually. This project aims to trial a lobster trap which will encourage fishers to alter their fishing behaviour thereby increasing their CPUE which translates directly to cost savings in fuel and bait usage.

The decision to use more efficient pots could be undertaken at an individual fisher level, but this requires robust conversion rates for any modified design(s) to ensure that the integrity of the fishery's input based management system is not compromised. The potential for further cost savings arising through the purchase and maintenance of licences containing lesser numbers of entitlements is also likely.

Objectives

1. To calculate the potential cost savings which arise through the use of a reduced number of more efficient 1.2m lobster traps in tandem with a modified fishing behaviour. These estimates would be derived by obtaining attaining robust estimates of catch rates (catch per unit effort) using the 1.2m trap compared to traditional pots in the fishery combined with the estimated reduction in operating costs that would arise from the widespread adoption of the 1.2m traps. For instance, a fisherman choosing to deploy a 1.2m trap that is 20% more efficient than traditional methods would lose 20% of his entitlements. This analysis would incorporate both varying estimates of efficiency and degree of uptake by industry.
2. To determine whether a modified 1.2m lobster trap will alter the fishing behaviour of the WRL fleet which is traditionally focused on 24 hour soak times. This would be achieved through an increased reliance on a trap which is greater in volume than the traditional pot, retains 100% of animals and ideally suited to extended soak times i.e. 48 – 72 hours.

Final report

ISBN: 978-0-9807845-9-6
Authors: Andrew Winzer Roy Melville-Smith Simon de Lestang & Adrian Thomson
Final Report • 2011-03-01 • 961.56 KB
2008-900-DLD.pdf

Summary

This project investigated the efficiency of using different pot designs to increase the profitability of the Western Rocklobster fishery. The motivation for this study was a more efficient pot would reduce the number of pot hauls, and that this in turn would increase profitability of the fishery by reducing the amount of bait used, the amount of time at sea, fuel usage and overall wear and tear on equipment.

During the course of this project, three different pot designs were trialed against the standard batten pot design. Trials of the new pot designs were undertaken in more than one management zone and for one (and more than one) day soaking times. In nearly all instances, standard batten pots proved to be more successful in catching lobsters than the two of the trialed pot designs. However, the third design, a side entrance batten pot with a broad base, hereafter termed the 'broad based pot', proved to be more effective than standard pots under particular conditions. In trials conducted during the reds part of the 2008/09 season, catches of legal sized lobsters made by broad based pots were not significantly different to those made by standard pots for one day and greater than one day soaking times. However, the broad based pots tended to catch fewer undersized lobsters. Trials of the broad based pots during the early part of the 2009/10 whites season showed that while they were not significantly different in terms of their ability over standard pots to catch legal sized lobsters on one day soaking periods, they were superior to the standard pot on two day soaks. The broad based pot design also caught significantly fewer under sized lobsters over two day soaking periods.

These results suggest that the use of broad based pots during the whites fishing season combined with longer pot soaking times would be expected to lead to multi-million dollar cost savings through reduced pot lifts. Furthermore, there would be a substantial reduction in the handling of hundreds of thousands of sub-legal discarded lobsters which could be expected to have beneficial flow-on effects in terms of future catch.

Final Report • 2011-03-01 • 961.56 KB
2008-900-DLD.pdf

Summary

This project investigated the efficiency of using different pot designs to increase the profitability of the Western Rocklobster fishery. The motivation for this study was a more efficient pot would reduce the number of pot hauls, and that this in turn would increase profitability of the fishery by reducing the amount of bait used, the amount of time at sea, fuel usage and overall wear and tear on equipment.

During the course of this project, three different pot designs were trialed against the standard batten pot design. Trials of the new pot designs were undertaken in more than one management zone and for one (and more than one) day soaking times. In nearly all instances, standard batten pots proved to be more successful in catching lobsters than the two of the trialed pot designs. However, the third design, a side entrance batten pot with a broad base, hereafter termed the 'broad based pot', proved to be more effective than standard pots under particular conditions. In trials conducted during the reds part of the 2008/09 season, catches of legal sized lobsters made by broad based pots were not significantly different to those made by standard pots for one day and greater than one day soaking times. However, the broad based pots tended to catch fewer undersized lobsters. Trials of the broad based pots during the early part of the 2009/10 whites season showed that while they were not significantly different in terms of their ability over standard pots to catch legal sized lobsters on one day soaking periods, they were superior to the standard pot on two day soaks. The broad based pot design also caught significantly fewer under sized lobsters over two day soaking periods.

These results suggest that the use of broad based pots during the whites fishing season combined with longer pot soaking times would be expected to lead to multi-million dollar cost savings through reduced pot lifts. Furthermore, there would be a substantial reduction in the handling of hundreds of thousands of sub-legal discarded lobsters which could be expected to have beneficial flow-on effects in terms of future catch.

Final Report • 2011-03-01 • 961.56 KB
2008-900-DLD.pdf

Summary

This project investigated the efficiency of using different pot designs to increase the profitability of the Western Rocklobster fishery. The motivation for this study was a more efficient pot would reduce the number of pot hauls, and that this in turn would increase profitability of the fishery by reducing the amount of bait used, the amount of time at sea, fuel usage and overall wear and tear on equipment.

During the course of this project, three different pot designs were trialed against the standard batten pot design. Trials of the new pot designs were undertaken in more than one management zone and for one (and more than one) day soaking times. In nearly all instances, standard batten pots proved to be more successful in catching lobsters than the two of the trialed pot designs. However, the third design, a side entrance batten pot with a broad base, hereafter termed the 'broad based pot', proved to be more effective than standard pots under particular conditions. In trials conducted during the reds part of the 2008/09 season, catches of legal sized lobsters made by broad based pots were not significantly different to those made by standard pots for one day and greater than one day soaking times. However, the broad based pots tended to catch fewer undersized lobsters. Trials of the broad based pots during the early part of the 2009/10 whites season showed that while they were not significantly different in terms of their ability over standard pots to catch legal sized lobsters on one day soaking periods, they were superior to the standard pot on two day soaks. The broad based pot design also caught significantly fewer under sized lobsters over two day soaking periods.

These results suggest that the use of broad based pots during the whites fishing season combined with longer pot soaking times would be expected to lead to multi-million dollar cost savings through reduced pot lifts. Furthermore, there would be a substantial reduction in the handling of hundreds of thousands of sub-legal discarded lobsters which could be expected to have beneficial flow-on effects in terms of future catch.

Final Report • 2011-03-01 • 961.56 KB
2008-900-DLD.pdf

Summary

This project investigated the efficiency of using different pot designs to increase the profitability of the Western Rocklobster fishery. The motivation for this study was a more efficient pot would reduce the number of pot hauls, and that this in turn would increase profitability of the fishery by reducing the amount of bait used, the amount of time at sea, fuel usage and overall wear and tear on equipment.

During the course of this project, three different pot designs were trialed against the standard batten pot design. Trials of the new pot designs were undertaken in more than one management zone and for one (and more than one) day soaking times. In nearly all instances, standard batten pots proved to be more successful in catching lobsters than the two of the trialed pot designs. However, the third design, a side entrance batten pot with a broad base, hereafter termed the 'broad based pot', proved to be more effective than standard pots under particular conditions. In trials conducted during the reds part of the 2008/09 season, catches of legal sized lobsters made by broad based pots were not significantly different to those made by standard pots for one day and greater than one day soaking times. However, the broad based pots tended to catch fewer undersized lobsters. Trials of the broad based pots during the early part of the 2009/10 whites season showed that while they were not significantly different in terms of their ability over standard pots to catch legal sized lobsters on one day soaking periods, they were superior to the standard pot on two day soaks. The broad based pot design also caught significantly fewer under sized lobsters over two day soaking periods.

These results suggest that the use of broad based pots during the whites fishing season combined with longer pot soaking times would be expected to lead to multi-million dollar cost savings through reduced pot lifts. Furthermore, there would be a substantial reduction in the handling of hundreds of thousands of sub-legal discarded lobsters which could be expected to have beneficial flow-on effects in terms of future catch.

Final Report • 2011-03-01 • 961.56 KB
2008-900-DLD.pdf

Summary

This project investigated the efficiency of using different pot designs to increase the profitability of the Western Rocklobster fishery. The motivation for this study was a more efficient pot would reduce the number of pot hauls, and that this in turn would increase profitability of the fishery by reducing the amount of bait used, the amount of time at sea, fuel usage and overall wear and tear on equipment.

During the course of this project, three different pot designs were trialed against the standard batten pot design. Trials of the new pot designs were undertaken in more than one management zone and for one (and more than one) day soaking times. In nearly all instances, standard batten pots proved to be more successful in catching lobsters than the two of the trialed pot designs. However, the third design, a side entrance batten pot with a broad base, hereafter termed the 'broad based pot', proved to be more effective than standard pots under particular conditions. In trials conducted during the reds part of the 2008/09 season, catches of legal sized lobsters made by broad based pots were not significantly different to those made by standard pots for one day and greater than one day soaking times. However, the broad based pots tended to catch fewer undersized lobsters. Trials of the broad based pots during the early part of the 2009/10 whites season showed that while they were not significantly different in terms of their ability over standard pots to catch legal sized lobsters on one day soaking periods, they were superior to the standard pot on two day soaks. The broad based pot design also caught significantly fewer under sized lobsters over two day soaking periods.

These results suggest that the use of broad based pots during the whites fishing season combined with longer pot soaking times would be expected to lead to multi-million dollar cost savings through reduced pot lifts. Furthermore, there would be a substantial reduction in the handling of hundreds of thousands of sub-legal discarded lobsters which could be expected to have beneficial flow-on effects in terms of future catch.

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